US5433933A - Method of purifying oxygen-excess exhaust gas - Google Patents
Method of purifying oxygen-excess exhaust gas Download PDFInfo
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- US5433933A US5433933A US08/176,290 US17629093A US5433933A US 5433933 A US5433933 A US 5433933A US 17629093 A US17629093 A US 17629093A US 5433933 A US5433933 A US 5433933A
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- zeolite
- cobalt
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- earth metal
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9445—Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC]
- B01D53/945—Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC] characterised by a specific catalyst
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J29/00—Catalysts comprising molecular sieves
- B01J29/04—Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
- B01J29/06—Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
- B01J29/064—Crystalline aluminosilicate zeolites; Isomorphous compounds thereof containing iron group metals, noble metals or copper
- B01J29/072—Iron group metals or copper
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02T—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO TRANSPORTATION
- Y02T10/00—Road transport of goods or passengers
- Y02T10/10—Internal combustion engine [ICE] based vehicles
- Y02T10/12—Improving ICE efficiencies
Definitions
- the present invention relates to a catalyst for and a method of purifying an exhaust gas containing an excess amount of oxygen, to remove nitrogen oxides (NO x ), carbon monoxide and hydrocarbons therefrom.
- the present invention is particularly applied to the purification of exhaust gases originated from internal combustion engines of automobiles and nitric acid production plants.
- a three-way catalyst which consists of platinum (Pt), rhodium (Rh), palladium (Pb) or other noble metals supported on a carrier material such as alumina (Al 2 O 3 ) is used.
- Pt platinum
- Rh rhodium
- Pb palladium
- a carrier material such as alumina (Al 2 O 3 )
- oxygen-excess exhaust gas or "exhaust gas containing an excess amount of oxygen” is intended to mean that the exhaust gas contains an excess amount of oxygen beyond the amount necessary to completely oxidize carbon monoxide, hydrocarbons and hydrogen in the exhaust gas.
- a catalyst having a transition metal introduced through an ion exchange on a zeolite substrate it is also well-known to use a catalyst having a transition metal introduced through an ion exchange on a zeolite substrate.
- Japanese Unexamined Patent Publication (Kokai) No. 130735/1989 teaches a copper (Cu)-containing zeolite catalyst wherein Cu is introduced into the zeolite structure through an ion exchange.
- the described catalyst when used to selectively reduce nitrogen oxides (NO x ) from an oxygen-excess atmosphere, which also contains unburned carbon monoxide and hydrocarbons, can effectively reduce the nitrogen oxides to nitrogen (N 2 ), a nontoxic substance.
- the Cu-containing catalyst can exhibit a satisfactory NO x reducing capability at a temperature of 200° C. or more, but suffers from the following drawbacks:
- An initial catalytic activity of the Cu-containing zeolite catalyst is very high, because of good adsorption capability of Cu for NO x , but a durability of the catalyst, especially at an elevated temperature is poor. Namely, the high catalytic activity of the catalyst is notably deteriorates when the catalyst is exposed to a high temperature condition for a long time. Therefore, there is a need to provide an improved catalyst with an excellent catalytic activity which is not deteriorated when used for a long time.
- the Cu-containing zeolite catalyst has such an insufficient durability only because Cu can migrate and aggregate in the zeolite at a temperature of about 600° C. or more, to thereby cause a loss of the catalytic activity of the catalyst, and a stability of the catalyst structure is lowered as a result of the presence of the contained Cu, and accordingly, the catalyst structure itself is destroyed after a long term use of the catalyst.
- One object of the present invention is to solve the problems of the above-described prior art catalysts for purifying an exhaust gas, and more particularly, to provide an improved catalyst for purifying an exhaust gas containing an excess amount of oxygen such as that originated from an internal combustion engine of automobiles and nitric acid production plants, to simultaneously reduce nitrogen oxides (NO x ), carbon monoxide (CO) and hydrocarbons (HC) therefrom.
- This catalyst in comparison with the prior art catalysts, has an excellent durability and therefore, maintains an excellent catalytic activity and purification capability thereof, without deterioration thereof, under high temperature conditions and for a long time.
- the catalyst has a stability over a wide range of temperature.
- Another object of the present invention is to provide an improved method of purifying an exhaust gas containing an excess amount of oxygen.
- the exhaust gas to be purified is, as previously described, that emitted from the internal combustion engine such as diesel engine or gasoline engine, of automobiles or nitric acid production plants, for example.
- a catalyst for purifying an exhaust gas containing an excess amount of oxygen to reduce nitrogen oxides, carbon monoxide and hydrocarbons therefrom the zeolite used as a principal component of the catalyst being represented by the general formula:
- M is a cation
- n is a valency of the cation M
- x 0.8 to 2
- y is at least 2
- the catalyst comprises a zeolite having a molar ratio of SiO 2 to Al 2 O 3 of at least 15, and containing cobalt alone or in combination with at least one metal selected from alkali earth metals and rare earth metals.
- a method of purifying an exhaust gas containing an excess amount of oxygen which comprises bringing the described catalyst into contact with the exhaust gas to reduce nitrogen oxides, carbon monoxide and hydrocarbons therefrom.
- the zeolite used as a principal component of the catalyst is represented by the general formula:
- M is a cation
- n is a valency of the cation M
- x 0.8 to 2
- y is at least 2
- z is at least zero (0), preferably 2 to 7. Because of the specific three-dimensional net structure thereof, the zeolite has both an cation exchange capability and a molecular sieve function, and these properties are a basis for the use of the zeolite as a catalyst.
- the zeolite used in the present invention includes both naturally occurring substances and synthesized substances, and when synthesized, the zeolite may be produced by using any conventional production process.
- Typical examples of the zeolite which can be advantageously used in the practice of the present invention include ferrierite, zeolite Y, ZSM-type zeolites such as ZSM-5, ZSM-11, ZSM-12 and ZSM-20, and other zeolites.
- these zeolites may be used without treatment thereof or as produced or if desired, may be treated to obtain an ion exchanged zeolite.
- the zeolite may be treated with an ammonium salt and mineral acid to obtain an NH 4 + -type and H + -type ion exchanged zeolite, respectively.
- the zeolite used in the present invention contains silicon dioxide (SiO 2 ) and alumina (Al 2 O 3 ) in a molar ratio of SiO 2 to Al 2 O 3 of at least 15, and carrying cobalt alone or in combination with at least one metal selected from alkali earth metals and rare earth metals.
- the molar ratio of SiO 2 to Al 2 O 3 in the zeolite is preferably 15 to 1,000, and the metal carried on the zeolite is cobalt (Co) in a molar amount which is 0.9 to 1.6 times higher than the molar amount of alumina.
- the term "molar amount of Co" used herein means a mole number of Co compared with the mole number of alumina.
- a molar ratio of SiO 2 /Al 2 O 3 in the zeolite is at least 15, but the upper value thereof is not limited, although as previously mentioned the range of from 15 to 1,000 is preferred.
- the molar ratio of SiO 2 /Al 2 O 3 below 15 should be avoided. This is because the zeolite having SiO 2 /Al 2 O 3 ratio of less than 15 has a poor heat resistance and durability.
- the zeolite catalyst according to this first preferred embodiment of the present invention contains cobalt (Co) introduced therein, and such a catalyst is referred to herein as a cobalt (Co)-containing zeolite catalyst.
- Co cobalt
- the former is 0.9 to 1.6 times higher than the latter.
- the molar amount of less than 0.9 times should be avoided, because it cannot ensure the production of a zeolite catalyst showing a diminished thermal deterioration and having a high durability.
- the molar amount of more than 1.6 times should be also avoided, because it cannot ensure the production of a zeolite catalyst having a high activity and durability. More particularly, it is considered that a molar amount of the cobalt of less than 0.9 times induces a reduced catalytic activity due to a limited amount of cobalt, which can act as an active point of the catalyst, and that of more than 1.6 times causes a clogging of fine pores opened on an outer surface of the zeolite, because a large amount of cobalt can adhere to the outer surface of the zeolite, and accordingly, the zeolite catalyst has a poor catalytic activity.
- cobalt (Co) into the zeolite can be carried out in accordance with any conventional methods; typically by an ion exchange method or impregnation method.
- the cobalt is preferably used in the form of a water-soluble salt thereof, and example of useful water-soluble salts include cobalt nitrate, cobalt chloride, cobalt acetate and cobalt sulfate.
- the ion exchange method is preferably loaded out by repeating an ion exchange treatment of zeolite with cobalt (II) salt two or more times.
- This repeated ion exchange ensures a further improvement of the durability of the resulting catalyst, in addition to an improvement of the durability obtained by the introduction of cobalt in a molar amount of 0.9 to 1.6 times higher than that of alumina.
- the ion exchange treatment when the ion exchange treatment is not repeated, i.e., a single ion exchanging step is applied, it is very difficult to obtain the proper introduction of cobalt in a molar amount of 0.9 to 1.6 times.
- the single ion exchange step has problems such that a sufficient amount of the cobalt is not introduced into the zeolite, and that a bonding strength of the cobalt to ion exchange site(s) of the zeolite is not high, and therefore, the cobalt can be easily separated from the ion exchange site(s) upon an application of heat.
- the impregnation method is preferably carried out, for example, by dipping the zeolite in an aqueous solution of the selected cobalt salt for about 1 to 2 hours, drying the dipped zeolite in an atmosphere, and if desired finally calcining it at an elevated temperature such as 500° C., whereby a satisfactory catalyst can be obtained.
- the catalyst obtained in accordance with this impregnation method exhibits an excess adhesion of the cobalt ion onto only an outer surface of the zeolite, and therefore, only an insufficient and limited introduction of the cobalt ion into the ion exchange site(s).
- the cobalt is preferably used as water-soluble salts thereof, for example, nitrate, chloride, acetate and sulfate of cobalt (II). More preferably, cobalt (II) acetate is used in the introduction of the cobalt ion into the zeolite to thereby produce the desired catalyst showing no or less thermal deterioration and having a high level of durability.
- cobalt (II) nitrate, chloride or sulfate is used as the source material of cobalt, it is necessary to repeat the described ion exchange steps at least five times, to obtain the molar amount of cobalt of at least 0.9 times of that of alumina in the zeolite. This is because, with these cobalt (II) salts, the ion exchange of the cobalt in the zeolite progresses little in comparison with the case of cobalt (II) acetate.
- the time for conducting the ion exchange is not limited to a certain range, and therefore, can be widely varied depending upon the specific ion exchange conditions desired results and other factors. Nevertheless, the ion exchange is preferably carried out for a time per step of 5 hours or more, more preferably 10 hours or more. An ion exchange time shorter than 5 hours should be avoided, because it is accompanied by a notable reduction of the ion exchange efficiency. Note, in such a case, and when cobalt (II) acetate is used as a source material, it is essential to repeat the ion exchanging step at least five times, to obtain satisfactory results.
- the ion exchange treatment can be carried out, for example, by adding a salt of cobalt (II) to a slurry of zeolite and stirring the mixture, or by adding the zeolite to an aqueous solution containing a salt of cobalt (II) and stirring the mixture.
- a temperature of the solution or system is preferably in the range of 50° to 100° C., more preferably 60° to 90° C.
- the cobalt salt is preferably used as an aqueous solution thereof, and a concentration of the cobalt salt in the aqueous solution is preferably in the range of 0.01 to 1 mole/l, more preferably 0.1 to 1 mole/l.
- a concentration below 0.01 mole/l will reduce the operability of the ion exchange process, because a remarkably larger amount of the solution must be used to control an amount of the cobalt to a desired level. Further, a concentration above 1 mole/l will not result in a significant improvement of the ion exchange efficiency despite of the supply of more than the necessary amount of the cobalt salt.
- the excessively increased concentration of the cobalt salt will cause a problem in that a larger amount of cobalt is selectively loaded on an outer surface of the zeolite, and thus the micropores of the zeolite are clogged because a solubility of the cobalt salt in water is relatively low.
- the ion exchange is completed after repeating the above-described ion exchanging steps two or more times. Nevertheless, if a molar ratio of CoO/Al 2 O 3 in the ion-exchanged zeolite is smaller than the lower limit thereof, i.e., 0.9, it is preferable to further mix the ion-exchanged zeolite with an aqueous solution containing enough the cobalt to adjust the molar ratio of CoO/Al 2 O 3 to the range of from 0.9 to 1.6, and to evaporate the water in the mixture to dryness.
- the evaporation the water to dryness of the mixture can be carried out by any conventional method, for example, the zeolite is added to an aqueous solution containing the cobalt salt, and the solution is dried in a drying oven or similar apparatus to evaporate the water used as a solvent.
- a preferred concentration of the cobalt salt in the aqueous solution is 0.01 mole/l or more, as a concentration of less than 0.01 mol/l requires an extended water evaporation time.
- An upper limit of the concentration of the cobalt salt is not critical, but generally the concentration should not exceed 0.5 mol/l, because a higher concentration of the cobalt salt prevents a uniform adhesion of the cobalt to the zeolite.
- the treated zeolite is subjected to a solid-liquid separation, followed by washing and drying.
- the dried product can be used as a catalyst for the purification of an exhaust gas, and if desired, may be calcined at a suitable elevated temperature.
- a molar ratio of SiO 2 /Al 2 O 3 thereof is substantially the same as that of the zeolite used as the starting substrate, and a crystalline structure of the catalyst is substantially the same as that of the zeolite. Namely, before and after the ion exchange, the crystalline structure of the zeolite is not substantially changed.
- the cobalt (Co)-containing zeolite catalyst of the present invention can be further treated, if desired.
- the catalyst may be molded into any desired shape, such as a powdered body, pellet structure and honeycomb structure.
- the powder-like catalyst may be admixed with a binding agent such as clay, minerals, alumina sol and silica sol, followed by molding the admixture into any desired shape or structure.
- a binding agent such as clay, minerals, alumina sol and silica sol
- Suitable example of the clay and minerals used as the binding agent include kaolin, attapulgite, montmorillonite, bentonite, allophane and sepiolite.
- the catalyst may be directly molded into a binder-less molded product of zeolite.
- the cobalt ion may be introduced into the molded product of zeolite by using an ion exchange or other method.
- the catalyst may be mixed with water to prepare an aqueous slurry thereof, followed by wash-coating the slurry onto a honeycomb-structured refractory substrate such as ceramics, for example, cordierite or alumina, and metals.
- the Co-containing zeolite catalyst of the present invention can be widely used in the purification of various types of exhaust gas, with satisfactory results.
- the catalyst is particularly suited to the reduction of nitrogen oxides (NO x ), carbon monoxide (CO) and hydrocarbons (HC) from an oxygen-excess exhaust gas.
- oxygen-excess exhaust gas means an exhaust gas which contains an amount of oxygen in excess of the amount necessary to completely oxidize the CO, HC and hydrogen (H) in the exhaust gas, and includes those, for example, exhausted from the internal combustion engine of automobiles.
- a typical example of such an exhaust gas from the engine is an exhaust gas produced in the engine at a high air/fuel (A/F) ratio, i.e., lean condition.
- the catalyst of the present invention can be similarly applied to the purification of the non-oxygen-excess exhaust gas containing CO, HC and H 2 , without a change of the excellent performance thereof and with satisfactory results.
- the molar ratio of SiO 2 to Al 2 O 3 in the zeolite is at least 15, preferably 15 to 1,000, and the metal containing in the zeolite is cobalt (Co) and alkali earth metal.
- the alkali earth metal used in combination with the cobalt may be one metal or a combination of two or more metals.
- the molar ratio of SiO 2 to Al 2 O 3 has an lower limit of 15, but has no upper limit, and is preferably in the range of 15 to 1,000. Note, the SiO 2 /Al 2 O 3 ratio of less than 15 should be avoided, because it is cannot provide a catalyst having a satisfactory heat resistance and durability.
- the catalyst according to this second embodiment of the present invention contains cobalt (Co) and an alkali earth metal induced therein, and such catalyst is referred to herein as a cobalt (Co)- and alkali earth metal-containing zeolite catalyst.
- the cobalt and the alkali earth metal are preferably introduced into the zeolite in a molar amount which is 0.5 to 1.7 times and 0.1 to 1 times higher, respectively, than the molar amount of the alumina in the zeolite, and the total molar amount of the cobalt and alkali earth metal is 1.0 to 2.5 times higher than the molar amount of the alumina.
- the Co/Al 2 O 3 ratio of less than 0.5 will cause a problem in that the final product cannot be suitably used as a catalyst due to a low catalytic activity and the like, and a Co/Al 2 O 3 ratio of more than 1.7 will cause a problem in that the resulting catalyst does not exhibit a satisfactory durability and catalytic activity which will counterbalance the amount of the cobalt introduced to the zeolite.
- the alkali earth metal/Al 2 O 3 ratio of less than 0.1 often will provide the catalyst having only a slightly improved catalytic activity and durability, and with an alkali earth metal/Al 2 O 3 ratio of more than 1, often the resulting catalyst does not exhibit effects which will counterbalance the amount of alkali earth metal.
- the alkali earth metal introduced together with the cobalt (Co) into the zeolite can be freely selected, and is preferably selected from the group consisting of magnesium (Mg), calcium (Ca), strontium (Sr) and barium (Ba). As previously mentioned, these alkali earth metals may be used alone or in combination.
- cobalt (Co) and alkali earth metal into the zeolite can be carried out in accordance with any conventional method, typically an ion exchange method or impregnation method, but preferably, an ion exchange method.
- the cobalt is preferably used in the form of a water-soluble salt thereof, and example of useful water-soluble salts include cobalt nitrate, cobalt chloride, cobalt acetate and cobalt sulfate.
- cobalt acetate is preferably used.
- the alkali earth metal is preferably used in the form of a water-soluble salt thereof such as nitrate, chloride, acetate and sulfate. Nitrate and chloride are most preferred, because they have a high solubility in water.
- the ion exchange of the cobalt and alkali earth metal can be carried out in a manner similar to those described above with regard to the introduction of the cobalt into the zeolite.
- the sequence of the ion exchange for the cobalt and alkali earth metal is not restricted, but preferably the alkali earth metal is first introduced into the zeolite, followed by and the cobalt.
- the ion exchange of the alkali earth metal can be carried out in the same manner as for the above-described ion exchange of the cobalt.
- the ion exchange can be carried out by adding a salt of alkali earth metal to a slurry of zeolite and stirring the mixture, or by adding the zeolite to an aqueous solution containing a salt of alkali earth metal and stirring the mixture.
- a temperature of the solution or system is generally in the range of 20° to 100° C., preferably 40° to 90° C.
- the salt of alkali earth metal is preferably used as an aqueous solution thereof, and a concentration of the alkali earth metal in the aqueous solution is preferably in the range of 0.01 to 5 mole/l, more preferably 0.1 to 2 mole/l.
- a solid/liquid ratio of zeolite and aqueous solution is not restricted, and therefore, can be widely varied; with the proviso that stirring can be satisfactorily carried out without problem. Nevertheless, a concentration of the solid in the slurry is preferably in the range of 5 to 50%.
- the cobalt is preferably introduced into the zeolite from an aqueous salt of the cobalt salt such as cobalt acetate, wherein a concentration of the cobalt salt in the aqueous solution is preferably in the range of 0.01 to 1 mole/l, more preferably 0.1 to 1 mole/l.
- a concentration of the cobalt salt in the aqueous solution is preferably in the range of 0.01 to 1 mole/l, more preferably 0.1 to 1 mole/l.
- the alkali earth metal and cobalt each can be advantageously introduced into the zeolite by another technique, such as impregnation and an evaporation to dryness.
- the impregnation method can be carried out, for example, by dipping the zeolite in an aqueous solution of the selected cobalt salt and alkali earth metal salt for about 1 to 2 hours, drying the dipped zeolite in an atmosphere, and if desired, finally, calcining it at an elevated temperature such as 500° C.
- the method based on the evaporation to dryness can be carried out by a conventional manner.
- the zeolite can be carried out by mixing the zeolite with an aqueous solution containing the alkali earth metal and/or cobalt, and heating the mixture in a drier to evaporate the water used as the solvent.
- a concentration of the alkali earth metal or cobalt in the aqueous solution can be widely varied, but to obtain a uniform adhesion thereof to the zeolite, it is generally preferred that the concentration of each of the alkali earth metal and cobalt is in the range of 0.01 to 1 mole/l.
- the treated zeolite is followed by a solid-liquid separation, washing and drying.
- the dried product can be used as a catalyst for the purification of an exhaust gas, and if desired, can be calcined.
- the cobalt (Co)-, alkali earth metal-containing zeolite catalyst can be further treated, if desired, to obtain a molded product thereof or other articles.
- the Co-, alkali earth metal-containing zeolite catalyst can be widely used in the purification of various types of exhaust gases, with satisfactory results. Note, a detailed description of these points is omitted, since has it has been given hereinbefore with reference to the Co-containing zeolite catalyst.
- the molar ratio of SiO 2 to Al 2 O 3 in the zeolite is at least 15, preferably 15 to 1,000, and the metal containing in on the zeolite is cobalt (Co) and rare earth metal.
- the rare earth metal used in combination with the cobalt may be a single metal or a combination of two or more metals.
- the molar ratio of SiO 2 to Al 2 O 3 has a lower limit of 15 but has no upper limit, and is preferably in the range of 15 to 1,000. Note, the SiO 2 /Al 2 O 3 ratio of less than 15 should be avoided, because a zeolite catalyst having a satisfactory heat resistance and durability cannot be obtained.
- the catalyst according to this third embodiment of the present invention contains cobalt (Co) and rare earth metal induced therein, and such a catalyst is referred herein to as a cobalt (Co)-, rare earth metal-containing zeolite catalyst.
- the cobalt and rare earth metal are preferably introduced into the zeolite in a molar amount which is 0.5 to 1.7 times and 0.1 to 0.8 times higher, respectively, than the molar amount of the alumina in the zeolite, and the total molar amount of the cobalt and rare earth metal is 1.0 to 2.2 times higher than the molar amount of the alumina.
- the Co/Al 2 O 3 ratio of less than 0.5 will cause a problem in that the final product cannot be suitably used as a catalyst due to a lower catalytic activity and the like, and the Co/Al 2 O 3 ratio of more than 1.7 will cause a problem in that the resulting catalyst does not exhibit a satisfactory durability and catalytic activity which will counterbalance the amount of the cobalt introduced to the zeolite.
- the rare earth metal/Al 2 O 3 ratio of less than 0.1 often provides a catalyst having only a slightly improved catalytic activity and durability, and with the rare earth metal/Al 2 O 3 ratio of more than 0.8 often the resulting catalyst does not exhibit effects which will counterbalance the amount of the rare earth metal.
- the rare earth metal introduced together with the cobalt (Co) into the zeolite can be freely selected, but is preferably selected from the group consisting of lanthanum (La), cerium (Ce), yttrium (Y), praseodymium (Pr), samarium (Sm) and neodymium (Nd). As previously mentioned, these rare earth metals may be used alone or in combination.
- cobalt (Co) and rare earth metal into the zeolite can be carried out in accordance with any conventional method, typically an ion exchange method or impregnation method, most preferably, an ion exchange method.
- the cobalt is preferably used in the form of a water-soluble salt thereof, and example of useful water-soluble salts include cobalt nitrate, cobalt chloride, cobalt acetate and cobalt sulfate.
- cobalt acetate is preferably used.
- the rare earth metal is preferably used in the form of a water-soluble salt thereof such as nitrate, chloride, acetate and sulfate.
- nitrate and chloride are preferred, because they have a high solubility in water.
- the ion exchange of the cobalt and rare earth metal can be carried out in the same manner as described above with regard to the introduction of the cobalt into the zeolite.
- the sequence of the ion exchange for the cobalt and rare earth metal is not restricted, but preferably the rare earth metal is first introduced into the zeolite, followed by the cobalt.
- the ion exchange of the rare earth metal can be carried out in the same manner as for the above-described ion exchange of the cobalt.
- the ion exchange can be carried out by adding a salt of rare earth metal to a slurry of zeolite and stirring the mixture, or by adding the zeolite into an aqueous solution containing a salt of rare earth metal and stirring the mixture.
- a temperature of the solution or system is generally in the range of 20° to 100° C., preferably 40° to 90° C.
- the salt of rare earth metal is preferably used as an aqueous solution, and a concentration of the rare earth metal in the aqueous solution is preferably in the range of 0.01 to 5 mole/l, more preferably 0.1 to 2 mole/l.
- a solid/liquid ratio of zeolite and aqueous solution is not restricted, and therefore, can be widely varied as long as stirring can be satisfactorily carried out without problem. Nevertheless, a concentration of the solid in the slurry is preferably in the range of 5 to 50%.
- the cobalt is preferably introduced into the zeolite from an aqueous salt of the cobalt salt such as cobalt acetate, wherein a concentration of the cobalt salt in the aqueous solution is preferably in the range of 0.01 to 1 mole/l, more preferably 0.1 to 1 mole/l. The reason why the described range of the concentration of the cobalt salt is preferred has been given.
- the rare earth metal and cobalt each can be advantageously introduced into the zeolite by using other technique such as impregnation and evaporation to dryness.
- the impregnation method and the method based on the evaporation to dryness can be carried out in the same manner as described for the production of the Co-containing zeolite catalyst and the Co-, alkali earth metal-containing zeolite catalyst.
- the treated zeolite is subjected to a solid-liquid separation, followed by washing and drying.
- the dried product can be used as a catalyst for the purification of an exhaust gas, and if desired, can be calcined.
- the cobalt (Co)-, rare earth metal-containing zeolite catalyst can be further treated, if desired, to obtain a molded product thereof or other articles.
- the Co-, rare earth metal-containing zeolite catalyst can be widely used in the purification of various types of exhaust gases, with satisfactory results. Note, a detailed description of these points is omitted, since it has been mentioned hereinbefore with reference to the Co-containing zeolite catalyst.
- the molar ratio of SiO 2 to Al 2 O 3 in the zeolite is at least 15, preferably 15 to 1,000, and the metal containing in the zeolite is cobalt (Co), at least one alkali earth metal and at least one rare earth metal.
- the alkali earth metal and the rare earth metal used in combination with the cobalt may be a single metal or a combination of two or more metals.
- the catalyst according to this fourth embodiment of the present invention contains cobalt (Co), alkali earth metal and rare earth metal in combination induced therein, and such a catalyst is referred herein to as a cobalt (Co)-, alkali earth metal- and rare earth metal-containing catalyst.
- the catalyst described herein effectively purifies an oxygen-excess exhaust gas to simultaneously reduce nitrogen oxides (NO x ), carbon monoxide (CO) and hydrocarbons (HC) therefrom.
- the zeolite catalyst is effective for selectively reducing nitrogen oxides (NO x ) from the exhaust gas in an oxygen-excess atmosphere. Since it has a notably improved NO x reduction capability, compared with the prior art Cu-containing zeolite catalyst, the catalyst of the present invention can be advantageously utilized in the purification of the oxygen-excess exhaust gas from the nitric acid production plants, in addition to the purification of the exhaust gas from the internal combustion engine of automobiles.
- the surprisingly improved performances of the described catalyst are obtained as a function of the synergistic actions of the cobalt, alkali earth metal and rare earth metal.
- the cobalt has a capability of selectively adsorbing NO x thereon.
- the alkali earth metal and rare earth metal each has an action of accelerating a selective reaction of NO x and hydrocarbons (HC) on the cobalt, because each metal or a complex thereof with the zeolite can directly or indirectly adsorb the hydrocarbons thereon.
- HC hydrocarbons
- each of the excellent actions of the cobalt, alkali earth metal and rare earth metal can be effectively combined to give a superior performance catalyst.
- a durability of the catalyst is improved, because the alkali earth metal and rare earth metal can inhibit a formation of coke during the reaction of NO x and HC.
- the cobalt has an improved bonding strength thereof to the zeolite, and accordingly, has an improved durability.
- NO x activity and inhibit a formation of coke it becomes the alkali earth metal and rare earth metal are further incorporated into the zeolite, and these metals have a possible to improve the catalytic activity and durability of the resulting catalyst.
- the reason why the aggregation of the cobalt is prevented is also considered to be because the cobalt ion can easily react with the alkali earth metal and rare earth metal, to thereby form a perovskite-type complex oxide.
- the zeolite used as a principal component of the catalyst of the present invention is represented by the general formula (I), and is conventionally used as the catalyst because of its excellent cation exchange capability and molecular sieve function. More particularly, the zeolite has a tetrahedral network structure of SiO 4 and AlO 4 , in which each tetrahedral structure is bonded to the other through a crosslinking of oxygen on an edge portion thereof.
- the network structure of the zeolite therefore contains through-passages and through-cavities therein, and an ion exchangable cation such as H + , Na + or the like is introduced into ion exchange site(s) of the lattice having a negative charge.
- the molar ratio of SiO 2 to Al 2 O 3 in the zeolite has lower limit of 15, but has no upper limit, and is preferably in the range of 15 to 1,000.
- the preferred range of SiO 2 /Al 2 O 3 ratio is the same as that of the previously described Co-, alkali earth metal-containing zeolite catalyst and Co-, rare earth metal-containing zeolite catalyst, and in the present catalyst, the SiO 2 /Al 2 O 3 ratio of less than 15 causes a deterioration of the thermal stability of the catalyst at a higher temperature of 600° C.
- the SiO 2 /Al 2 O 3 ratio of more than 1,000 causes a reduction of the ion exchange level, i.e., catalytic activity, since the ion exchange site(s) are diminished as a result of a reduction of the Al 2 O 3 amount. Since the thermal deterioration is principally induced due to a change of the structure of the aluminum (Al) and surrounding areas, it is preferable to control the SiO 2 /Al 2 O 3 ratio in the zeolite to 20 or more (relatively small amount of Al 2 O 3 ), to thereby ensure a satisfactory durability under high temperature conditions.
- Typical examples of useful zeolites satisfying the above range of SiO 2 /Al 2 O 3 ratio include ZSM-5 having the SiO/Al 2 O 3 ratio of 20 to 200, zeolite Y and those having a mordenite structure.
- the previously mentioned NH 4 + and H + ion exchanged zeolites in which the ion exchange site(s) contain NH 4 + and H + ions bonded thereto, respectively can be advantageously used because NH 4 + and H + ions are easily ion-exchanged with the cobalt, alkali earth metal and rare earth metal ions.
- Na-type zeolite can be advantageously used.
- the zeolite surface contains micropores having a small pore size of 10 ⁇ or less.
- a small pore size is enough to prevent an undesirable introduction of polycyclic aromatic hydrocarbons into the pores of the zeolite, to thereby inhibit a formation of coke and prevent a destruction of the structure and reduction of the catalytic activity thereof due to a clogging of the pores.
- the alkali earth metal and rare earth metal introduced together with the cobalt (Co) into the zeolite can be freely selected, and the alkali earth metal is preferably selected from the group consisting of magnesium (Mg), calcium (Ca), strontium (Sr) and barium (Ba). More preferably, Mg, Ca, Sr and Ba are used as the alkali earth metal.
- the rare earth metal is preferably selected from the group consisting of lanthanum (La), cerium (Ce), yttrium (Y), praseodymium (Pr), samarium (Sm) and neodymium (Nd).
- the cobalt, alkali earth metal and rare earth metal are preferably introduced into the zeolite in an amount of 2.0 to 5.0% by weight, 0.05 to 10% by weight and 0.05 to 10% by weight, respectively, with regard to the weight of the zeolite.
- a cobalt content of less than 2.0% by weight should be avoided, because it does not ensure a satisfactory catalytic effect.
- the catalytic effect can be improved when the cobalt content is increased, but a cobalt content of above 5.0% by weight should be avoided because it causes an easy migration and aggregation of the cobalt, and thus a deterioration of the catalyst, in addition to an increase of the difficulty of introducing the alkali earth and rare earth metals.
- the alkali earth and rare earth metals are preferably used in the amount of 0.05 to 10% by weight, respectively. Namely, the effects induced with the addition of these metals can be found from the amount of 0.05% by weight. To obtain satisfactory effects, it is preferable to add these metals in an amount of 0.3% by weight or more, but an amount above 10% by weight should be avoided because it will reduce an acid point necessary to conduct the reaction between the NO x and HC, and thus retard the reaction itself. Note, generally, an optimum purification temperature for NO x is shifted to a high temperature side when the amount of the alkali earth and rare earth metals introduced is increased, and therefore, the amount of metals introduced should be increased in accordance with the conditions under which the catalysts are used.
- the introduction of the cobalt (Co), alkali earth metal and rare earth metal into the zeolite can be carried out in accordance with any conventional methods, such as ion exchange and/or impregnation. Note, since these conventional methods are described above with reference to the production of the cobalt (Co)-containing, Co- and alkali earth metal-containing, and Co- and rare earth metal-containing zeolite catalysts, a detailed description of the introduction process will be omitted herein.
- the cobalt and alkali earth and rare earth metals are preferably used in the form of a water-soluble salt thereof, more preferably, as an acetate or nitrate.
- the cobalt and alkali earth and rare earth metals may be simultaneously impregnated into the zeolite.
- the zeolite is dipped in an aqueous solution of the cobalt, alkali earth metal and rare earth metal, preferably acetate and or nitrate thereof, for 24 to 48 hours (ion exchanging step), and then the dipped zeolite is dried at 100° to 120° C. for about 10 hours.
- a temperature of the solution or system is 20° to 100° C., preferably 40° to 90° C. If desired, the ion exchange step may be repeated, and the number of the repetitions of the ion exchange steps is determined by various factors, such as the desired efficiency of the ion exchange.
- this ion exchange method is based on the phenomenon that ions of the cobalt and alkali earth and rare earth metals are ion-exchanged with cations of the zeolite, and thus the former ions are strongly bonded to the zeolite.
- the impregnation method can be carried out, for example, by dipping the zeolite in an aqueous solution such as used in the above ion exchange method, for about 1 to 2 hours, drying the dipped zeolite in the atmosphere, and finally, calcining it an elevated temperature such as 500° C.
- the treated zeolite is subtracted to solid-liquid separation, followed by washing and drying.
- the dried product can be used as a catalyst for the purification of an exhaust gas, and if desired, can be calcined.
- the cobalt (Co)-, alkali earth metal- and rare earth metal-containing zeolite catalyst can be further treated, if desired, to obtain a molded product thereof, or other articles.
- the catalyst of the present invention may have different shapes and structures, such as a powdered body, pellets and honeycomb body, as well as a composite body comprising a refractory substrate such as a honeycomb-structure alumina body and a coating of the catalyst applied from an aqueous slurry of the catalyst.
- the Co-, alkali earth metal- and rare earth metal-containing zeolite catalyst can be widely used in the purification of various types of exhaust gases, with satisfactory results. Note, a detailed description of these points is omitted, since it has been mentioned hereinbefore with reference to other types of catalysts according to the present invention.
- the last-mentioned catalyst of the present invention is particularly intended to purify the NO x in the exhaust gas through a reaction between the NO x and the unburned hydrocarbons or partially burned products thereof containing oxygen.
- the hydrocarbons and other substances involved in the purification process may be those originally contained in the exhaust gas. Nevertheless, if an amount of such substances in the exhaust gas is considered to be relatively low, additional hydrocarbons from the outside may be added to the exhaust gas.
- Catalyst No. 1 A chemical analysis of the thus obtained catalyst (hereinafter referred to as Catalyst No. 1) indicated that Catalyst No. 1 contains the cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.09.
- Example 2 The procedure of Example 1 was repeated except that the concentration of the aqueous solution of cobalt (II) acetate.tetrahydrate was increased to 0.5 mole/l, and the ion exchange steps were repeated three times (5 hours ⁇ 2, 16 hours ⁇ 1).
- Catalyst No. 2 A chemical analysis of the thus obtained catalyst (hereinafter referred to as Catalyst No. 2) indicated that Catalyst No. 2 contains cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.46.
- Example 1 The procedure of Example 1 was repeated except that the concentration of the aqueous solution of cobalt (II) acetate.tetrahydrate was increased to 0.5 mole/l, and the ion exchange steps were repeated two times (10 hours '2).
- the thus obtained zeolite catalyst contained cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 0.94.
- Catalyst No. 3 An amount of 20 g of the above zeolite catalyst was added to 34 ml of an aqueous solution of cobalt (II) nitrate.hexahydrate containing the cobalt in an amount corresponding to 1% by weight of metallic cobalt. The mixture was first dried at 85° C. for 10 hours, and then dried at 110° C. for 10 hours to be evaporated to dryness. A chemical analysis of the residue (hereinafter referred to as Catalyst No. 3) indicated that Catalyst No. 3 contains cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.37.
- Catalyst No. 4 An amount of 20 g of NH 4 + ion exchanged ZSM-5 having a molar ratio of SiO 2 /Al 2 O 3 of 40 was mixed with an aqueous solution of cobalt (II) nitrate.tetrahydrate (concentration: 0.1 mole/l).
- the aqueous solution used herein was previously weighed to adjust the cobalt content with regard to mole numbers of the alumina in the zeolite as the starting material to 1.2 times.
- the mixture was stirred at a room temperature for 16 hours, and then dried at 85° C. for 12 hours, followed by drying at 110° C. for 12 hours.
- Catalyst No. 4 A chemical analysis of the thus obtained catalyst (hereinafter referred to as Catalyst No. 4) indicated that Catalyst No. 4 contains cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.19.
- Comparative Catalyst No. 1 A chemical analysis of the thus obtained catalyst (hereinafter referred to as Comparative Catalyst No. 1) indicated that Comparative Catalyst No. 1 contains cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 0.79.
- Comparative Catalyst No. 2 A chemical analysis of the thus obtained catalyst (hereinafter referred to as Comparative Catalyst No. 2) indicated that Comparative Catalyst No. 2 contains cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 2.54.
- Example 3 The procedure of Example 1 was repeated except that the concentration of the aqueous solution of cobalt (II) aetate-tetrahydrate was reduced to 0.23 mole/l, and the ion exchange step was not repeated (20 hours ⁇ 1).
- a chemical analysis of the thus obtained catalyst indicated that Comparative Catalyst No. 1 contains cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 0.84.
- An amount of 20 g of NH 4 + ion exchanged ZSM-5 having a molar ratio of SiO 2 /Al 2 O 3 of 40 was mixed with an aqueous solution of copper (II) acetate.hydrate (concentration: 0.1 mole/l), and, immediately after the mixing of the zeolite, a 2.5% amount of ammonia water was added to the aqueous solution to adjust a pH value thereof to 10.5.
- the aqueous solution used herein was previously weighed to adjust the copper content with regard to mole numbers of the alumina in the zeolite as the starting material to 2 times. The mixture was stirred at a room temperature for 16 hours.
- Comparative Catalyst No. 4 contains copper (II) in a molar ratio of CuO/Al 2 O 3 in the zeolite of 1.04.
- the zeolite catalyst was press-molded and then crushed to obtain a granular catalyst having a granule size of 12 to 20 meshes.
- An amount of 0.65 g of the granular catalyst was filled into an atmospheric pressure fixed bed flow type reaction tube.
- a gas having the following composition hereinafter referred to as a reaction gas
- a reaction gas was introduced at a flow rate of 600 ml/min. into the reaction tube, and the temperature in the reaction tube was elevated to 500° C. and held at that temperature for 30 minutes.
- reaction 1 After the pretreatment, the temperature of the reaction tube was reduced to 200° C. and then again elevated to 800° C. at an elevation rate of 5° C./min. (hereinafter, Reaction 1).
- the temperature of 800° C. was held for 5 hours, and then the reaction gas was replaced with a nitrogen (N 2 ) gas, and the reaction tube was left to stand for cooling.
- N 2 nitrogen
- the temperature in the reaction tube was reduced to a room temperature, the above-described reaction gas was introduced into the reaction tube, and the temperature of the reaction tube was elevated to 200° C. and held at that temperature for 30 minutes. Thereafter, the temperature of the reaction tube was elevated to 800° C. at an elevation rate of 5° C./min. (hereinafter, Reaction 2).
- NO in is a concentration of NO at an inlet of the reaction tube
- NO out is a concentration of NO at an outlet of the reaction tube.
- the catalysts according to the present invention can maintain an excellent exhaust gas purification capability in oxygen-excess exhaust gas, without a substantial lowering thereof, after use at 800° C. for 5 hours. Namely, the catalysts of the present invention have a remarkably excellent heat resistance and durability. These results suggest that the catalysts of the present invention can be advantageously used in the purification of oxygen-excess exhaust gas containing nitrogen oxides (NO x ), carbon monoxide (CO) and hydrocarbons (HC).
- NO x nitrogen oxides
- CO carbon monoxide
- HC hydrocarbons
- Catalyst No. 5 A chemical analysis of the thus obtained catalyst (hereinafter referred to as Catalyst No. 5) indicated that Catalyst No.
- Example 5 The procedure of Example 5 was repeated except that the barium chloride was replaced with the corresponding strontium salt.
- Catalyst No. 6 A chemical analysis of the thus obtained catalyst (hereinafter referred to as Catalyst No. 6) indicated that the Catalyst No. 6 contains the strontium in a molar ratio of SrO/Al 2 O 3 in the zeolite of 0.23 and the cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.12, respectively.
- Example 5 The procedure of Example 5 was repeated except that the barium chloride was replaced with the corresponding magnesium salt.
- Catalyst No. 7 A chemical analysis of the thus obtained catalyst (hereinafter referred to as Catalyst No. 7) indicated that the Catalyst No. 7 contains the magnesium in a molar ratio of MgO/Al 2 O 3 in the zeolite of 0.18 and the cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.08, respectively.
- Example 5 The procedure of Example 5 was repeated except that the barium chloride was replaced with the corresponding calcium salt.
- Catalyst No. 8 A chemical analysis of the thus obtained catalyst (hereinafter referred to as Catalyst No. 8) indicated that the Catalyst No. 8 contains the calcium in a molar ratio of CaO/Al 2 O 3 in the zeolite of 0.16 and the cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.04, respectively.
- Catalyst No. 9 contains the barium in a molar ratio of BaO/Al 2 O 3 in the zeolite of 0.58 and the cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.22, respectively.
- Catalyst No. 10 20 g of the above zeolite catalyst was mixed with 29 ml (0.05 mole/l) of an aqueous solution of barium nitrate containing the barium in an amount corresponding to 1% by weight of metallic barium. The mixture was first dried at 85° C. for 10 hours, and then dried at 110° C. for 10 hours, for an evaporation to dryness.
- Catalyst No. 10 The thus obtained catalyst is hereinafter referred to as Catalyst No. 10.
- Comparative Catalyst No. 5 contains the cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.39.
- Comparative Catalyst No. 6 An amount of 20 g of NH 4 + ion exchanged ZSM-5 having a molar ratio of SiO 2 /Al 2 O 3 of 40 mixed with 180 g of an aqueous solution of barium chloride (concentration: 1.09 mole/l), and the mixture was stirred at 80° C. for 16 hours. After the solid-liquid separation, the separated zeolite cake was thoroughly washed with water, and then dried at 110° C. for 10 hours. A chemical analysis of the thus obtained catalyst (hereinafter referred to as Comparative Catalyst No. 6) indicated that Comparative Catalyst No. 6 contains the barium in a molar ratio of BaO/Al 2 O 3 in the zeolite of 0.76.
- the catalysts according to the present invention compared with the comparative catalysts, can exhibit an excellent exhaust gas purification capability in an oxygen-excess exhaust gas as well as a remarkably excellent heat resistance and durability, both at the initial stage of purification and after purification at 800° C. for 5 hours.
- Catalyst No. 11 A chemical analysis of the thus obtained catalyst (hereinafter referred to as Catalyst No. 11) indicated that Catalyst No.
- 11 contains the lanthanum in a molar ratio of LaO/Al 2 O 3 in the zeolite of 0.33 and the cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.13, respectively.
- Catalyst No. 12 contains the cerium in a molar ratio of CeO/Al 2 O 3 in the zeolite of 0.13 and the cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.12, respectively.
- Example 11 The procedure of Example 11 was repeated except that the lanthanum chloride was replaced with the corresponding yttrium salt.
- Catalyst No. 13 A chemical analysis of the thus obtained catalyst (hereinafter referred to as Catalyst No. 13) indicated that the Catalyst No. 13 contains the yttrium in a molar ratio of YO/Al 2 O 3 in the zeolite of 0.12 and the cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.08, respectively.
- Example 11 The procedure of Example 11 was repeated except that the lanthanum chloride was replaced with the corresponding neodymium salt.
- Catalyst No. 14 A chemical analysis of the thus obtained catalyst (hereinafter referred to as Catalyst No. 14) indicated that the Catalyst No. 14 contains the neodymium in a molar ratio of NdO/Al 2 O 3 in the zeolite of 0.11 and the cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.04, respectively.
- Catalyst No. 15 contains the lanthanum in a molar ratio of LaO/Al 2 O 3 in the zeolite of 0.44 and the cobalt (II) in a molar ratio of CoO/Al 2 O 3 in the zeolite of 1.22, respectively.
- Catalyst No. 16 20 g of the above zeolite catalyst was poured into 29 ml (0.05 mole/l) of an aqueous solution of lanthanum nitrate containing the lanthanum in an amount corresponding to 1.9% by weight of metallic lanthanum. The mixture was first dried at 85° C. for 10 hours, and then dried at 110° C. for 10 hours to conduct an evaporation to dryness.
- Comparative Catalyst No. 7 An amount 20 g of NH 4 + ion exchanged ZSM-5 having a molar ratio of SiO 2 /Al 2 O 3 of 40 was mixed with 180 g of an aqueous solution of lanthanum chloride (concentration: 1.09 mole/l), and the mixture was stirred at 80° C. for 16 hours. After the solid-liquid separation, the separated zeolite cake was thoroughly washed with water, and then dried at 110° C. for 10 hours. A chemical analysis of the thus obtained catalyst (hereinafter referred to as Comparative Catalyst No. 7) indicated that Comparative Catalyst No. 7 contains the lanthanum in a molar ratio of LaO/Al 2 O 3 in the zeolite of 0.55.
- Powders of NH 4 + ion exchanged ZSM-5 having a molar ratio of SiO 2 /Al 2 O 3 of 40 were mixed with an aqueous solution containing the acetate and/or nitrate of cobalt, alkali earth metal and rare earth metal described in the following Table 4 in the described amount.
- the zeolite powders were dried at 110° C. for 10 hours.
- the dried zeolite powders were then calcined at 500° C. for 3 hours in air.
- the zeolite catalyst, as described in the following Table 4, referred to as one of Catalysts Nos. 17 to 27 was thus obtained.
- Powders of NH 4 + ion exchanged ZSM-5 having a molar ratio of SiO 2 /Al 2 O 3 of 40 were mixed with an aqueous solution containing the acetate and/or nitrate of at least one of cobalt, alkali earth metal and rare earth metal described in the following Table 5 in the described amount.
- the zeolite powders were dried at 110° C. for 10 hours.
- the dried zeolite powders were then calcined at 500° C. for 3 hours in air.
- the zeolite catalyst, as described in the following Table 5, referred to as one of Comparative Catalysts Nos. 8 to 14 was thus obtained.
- Comparative Example 8 The procedure of Comparative Example 8 was repeated except that the zeolite powders were mixed with an aqueous solution of copper (II) acetate for 5 minutes.
- each zeolite catalyst was pelletized and then exposed to a simulated exhaust gas of automobiles, i.e., model gas, having the following composition:
- the model gas was formulated so that it had a composition similar to that of the oxygen-excess exhaust gas from a lean burn automobile engine. Thereafter, the same model gas was introduced catalyst. This determination of the NO x conversion into the reaction tube filled with the catalyst, to determine a NO x conversion efficiency (%) of the efficiency was made in the manner described in the catalytic activity evaluation of Catalysts Nos. 1 to 4 and Comparative Catalysts Nos. 1 to 4. The results of the evaluation of the catalytic activity are summarized in the following Table 6.
- Catalyst No. 28 or 29 having the composition described in the following Table 7, dried at 110° C. for 10 hours, and then calcined at 500° C. for 3 hours in air.
- the zeolite catalyst, as described in the following Table 7, referred to as Catalyst No. 28 or 29 was thus obtained.
- Catalyst Bodies Nos. 1 and 2 To evaluate a catalytic activity of each of Catalyst No. 29 (Example 18) and Comparative Catalyst No. 16 (Example 10) under city cruising conditions, 500 g of powders of the zeolite catalyst, 700 g of silica gel (10% by weight of SiO 2 ) and 100 g of pure water were mixed, and a pH value of the mixture was adjusted with 2.5% ammonia water to a range of from 10 to 11. The resulting slurry of zeolite was coated at a coverage of 120 g/l over a honeycomb body of cordierite (0.7 l volume).
- the honeycomb bodies with the zeolite catalyst (Catalyst No. 29 and Comparative Catalyst No. 16) are referred to herein as Catalyst Bodies Nos. 1 and 2, respectively.
- the Catalyst Bodies Nos. 1 and 2 were tested with regard to the initial catalytic activity and durability thereof (change of the catalytic activity after 1,000 km cruising and 30,000 km cruising, respectively, of the automobile engine).
- the automobile used in these tests had a body weight of 1 ton and was provided with a 1,600 cc lean burn engine.
- the exhaust system of the test engine was charged with the Catalyst Body No. 1 or 2, and the engine run under simulated city cruising conditions. Namely, a maximum temperature of the exhaust gas at an inlet of the exhaust system was increased to about 800° C., and under this temperature condition, the engine was continuously run for a time corresponding to 1,000 km cruising and 30,000 km cruising.
- the results in this table indicate that, in contrast to the comparative catalyst body, the catalyst bodies of the present invention have a high purification capability for oxygen-excess exhaust gas and a significantly high durability. Note, the high purification efficiency of the catalyst body of the present invention was retained without a substantial change thereof.
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Abstract
Description
xM.sub.2/n O.Al.sub.2 O.sub.3.ySiO.sub.2.zH.sub.2 O (I)
xM.sub.2/n O.Al.sub.2 O.sub.3.ySiO.sub.2.zH.sub.2 O (I)
uHC+vNO.sub.2 →wH.sub.2 O+yCO.sub.2 +zN.sub.2
______________________________________ Composition of Reaction Gas ______________________________________ NO 700 ppm O.sub.2 4% CO 1000 ppm C.sub.3 H.sub.6 400 ppm H.sub.2 O 3% N.sub.2 balance ______________________________________
TABLE 1 ______________________________________ maximum catalytic maximum catalytic activity activity Catalyst (Reaction 1) (Reaction 2) ______________________________________ Catalyst No. 1 67 66 Catalyst No. 2 71 69 Catalyst No. 3 66 63 Catalyst No. 4 56 43 Comparative 38 22 Catalyst No. 1 Comparative 42 36 Catalyst No. 2 Comparative 42 34 Catalyst No. 3 Comparative 98 33 Catalyst No. 4 ______________________________________
TABLE 2 ______________________________________ maximum catalytic maximum catalytic activity activity Catalyst (Reaction 1) (Reaction 2) ______________________________________ Catalyst No. 5 85 79 Catalyst No. 6 82 78 Catalyst No. 7 75 71 Catalyst No. 8 78 71 Catalyst No. 9 73 72 Catalyst No. 10 75 72 Comparative 98 33 Catalyst No. 4 Comparative 67 66 Catalyst No. 5 Comparative 45 23 Catalyst No. 6 ______________________________________
TABLE 3 ______________________________________ maximum catalytic maximum catalytic activity activity Catalyst (Reaction 1) (Reaction 2) ______________________________________ Catalyst No. 11 83 78 Catalyst No. 12 79 76 Catalyst No. 13 70 67 Catalyst No. 14 70 70 Catalyst No. 15 77 69 Catalyst No. 16 81 73 Comparative 98 33 Catalyst No. 4 Comparative 67 66 Catalyst No. 5 Comparative 39 24 Catalyst No. 7 ______________________________________
TABLE 4 ______________________________________ Catalyst Composition and amount (wt. %) ______________________________________ Catalyst No. 17 Co(3) + La(2) + Ba(1) Catalyst No. 18 Co(3) + La(2) + Ca(1) Catalyst No. 19 Co(3) + La(2) + Mg(1) Catalyst No. 20 Co(3) + La(0.06) + Sr(1) Catalyst No. 21 Co(3) + La(0.1) + Sr(1) Catalyst No. 22 Co(3) + La(2) + Sr(1) Catalyst No. 23 Co(3) + La(5) + Sr(1) Catalyst No. 24 Co(3) + La(10) + Sr(1) Catalyst No. 25 Co(3) + La(2) + Sr(10) Catalyst No. 26 Co(3) + Pr(2) + Sr(1) Catalyst No. 27 Co(3) + Y(2) + Sr(1) ______________________________________
TABLE 5 ______________________________________ Catalyst Composition and amount (wt. %) ______________________________________ Comparative Catalyst No. 8 Co(3) Comparative Catalyst No. 9 Co(3) + La(2) Comparative Catalyst No. 10 Co(3) + Sr(2) Comparative Catalyst No. 11 Co(3) + La(0.03) + Sr(1) Comparative Catalyst No. 12 Co(3) + La(15) + Sr(1) Comparative Catalyst No. 13 Co(3) + La(2) + Sr(15) Comparative Catalyst No. 14 Co(3) + La(2) + Sr(20) Comparative Catalyst No. 15 Cu(3) ______________________________________
______________________________________ Component Amount (vol. %) ______________________________________ CO 0.1 H.sub.2 0.033 C.sub.3 H.sub.6 0.04 NO 0.05 NO.sub.2 0.017 O.sub.2 4.0 CO.sub.2 10.0 H.sub.2 O 3.0 N.sub.2 balance ______________________________________
TABLE 6 ______________________________________ Catalyst NO conversion efficiency (%) ______________________________________ Catalyst No. 17 45 Catalyst No. 18 44 Catalyst No. 19 44 Catalyst No. 20 45 Catalyst No. 21 52 Catalyst No. 22 56 Catalyst No. 23 62 Catalyst No. 24 51 Catalyst No. 25 54 Catalyst No. 26 44 Catalyst No. 27 46 Comparative Catalyst No. 8 36 Comparative Catalyst No. 9 41 Comparative Catalyst No. 10 40 Comparative Catalyst No. 11 33 Comparative Catalyst No. 12 34 Comparative Catalyst No. 13 41 Comparative Catalyst No. 14 35 Comparative Catalyst No. 15 30 ______________________________________
TABLE 7 ______________________________________ NO.sub.x conversion Catalyst Composition and amount (wt %) efficiency (%) ______________________________________ Catalyst Co(2.45) + La(1.6) + Ba(0.8) 52 No. 28 Catalyst Co(2.45) + La(1.6) + Sr(0.8) 58 No. 29 Comparative Cu(2.45) 35 Catalyst No. 16 ______________________________________
TABLE 8 ______________________________________ NO.sub.x conversion efficiency (%) Catalyst before test after 1,000 km after 30,000 km body (before cruising) cruising cruising ______________________________________ No. 1 60 58 56 No. 2 40 35 32 (Compara- tive) ______________________________________
Claims (6)
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US08/176,290 US5433933A (en) | 1989-12-21 | 1993-12-30 | Method of purifying oxygen-excess exhaust gas |
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JP1331740A JP2939484B2 (en) | 1989-12-21 | 1989-12-21 | Exhaust gas purification method |
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JP1337249A JP2901295B2 (en) | 1989-12-26 | 1989-12-26 | Exhaust gas purification catalyst and method of using the same |
JP02149203A JP3114982B2 (en) | 1990-06-07 | 1990-06-07 | Exhaust gas purification catalyst and method of using the same |
JP1-149203 | 1990-06-07 | ||
JP02264820A JP3026355B2 (en) | 1990-10-01 | 1990-10-01 | Exhaust gas purification catalyst |
JP2-264820 | 1990-10-01 | ||
US63128890A | 1990-12-20 | 1990-12-20 | |
US08/176,290 US5433933A (en) | 1989-12-21 | 1993-12-30 | Method of purifying oxygen-excess exhaust gas |
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Cited By (29)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5514355A (en) * | 1990-07-19 | 1996-05-07 | Tosoh Corporation | Method for purifying an oxygen-rich exhaust gas |
US5587137A (en) * | 1994-01-18 | 1996-12-24 | Corning Incorporated | Exhaust gas conversion method using thermally stable zeolites |
US5705136A (en) * | 1995-11-13 | 1998-01-06 | University Of Florida Research Foundation, Inc. | Catalyzed decomposition of nitrogen oxides on metal oxide supports |
WO1998000223A1 (en) * | 1996-07-03 | 1998-01-08 | Low Emissions Technologies Research And Development Partnership | Nitrogen oxide adsorbing material |
FR2757428A1 (en) * | 1996-12-21 | 1998-06-26 | Daimler Benz Ag | USE OF A CATALYST CONSISTING OF SEVERAL MATERIALS TO REDUCE NITROGEN OXIDES (NOX) IN OXYGEN GASES |
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CN110918117B (en) * | 2019-11-28 | 2023-03-21 | 浙江师范大学 | Catalyst for eliminating nitrogenous organic matters and preparation method thereof |
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US5514355A (en) * | 1990-07-19 | 1996-05-07 | Tosoh Corporation | Method for purifying an oxygen-rich exhaust gas |
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WO1999001203A1 (en) * | 1997-07-04 | 1999-01-14 | Metallgesellschaft Aktiengesellschaft | Method for producing fine-grained catalysts from natural zeolite |
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US6235255B1 (en) | 1999-05-21 | 2001-05-22 | Asec Manufacturing | Catalyst support having zeolite with high sodium back ion-exchange capacity and catalysts made therefrom |
US6314722B1 (en) | 1999-10-06 | 2001-11-13 | Matros Technologies, Inc. | Method and apparatus for emission control |
US6514470B1 (en) * | 1999-10-28 | 2003-02-04 | The Regents Of The University Of California | Catalysts for lean burn engine exhaust abatement |
WO2001030696A1 (en) * | 1999-10-28 | 2001-05-03 | The Regents Of The University Of California | Catalysts for lean burn engine exhaust abatement |
US6716783B2 (en) * | 1999-10-28 | 2004-04-06 | The Regents Of The University Of California | Catalysts for lean burn engine exhaust abatement |
US20030165415A1 (en) * | 1999-10-28 | 2003-09-04 | Ott Kevin C. | Catalysts for lean burn engine exhaust abatement |
US6555492B2 (en) | 1999-12-29 | 2003-04-29 | Corning Incorporated | Zeolite/alumina catalyst support compositions and method of making the same |
WO2003006364A3 (en) * | 2001-07-13 | 2003-09-25 | Chevron Usa Inc | Zeolite ssz-59 |
WO2003006364A2 (en) * | 2001-07-13 | 2003-01-23 | Chevron U.S.A. Inc. | Zeolite ssz-59 |
US6555080B1 (en) * | 2001-07-13 | 2003-04-29 | Chevron U.S.A. Inc. | Using zeolite SSZ-57 for reduction of oxides of nitrogen in a gas stream |
WO2003006369A1 (en) * | 2001-07-13 | 2003-01-23 | Chevron U.S.A. Inc. | Zeolite ssz-60 |
US6468485B1 (en) * | 2001-07-13 | 2002-10-22 | Chevron U.S.A. Inc. | Using zeolite SSZ-60 for reduction of oxides of nitrogen in a gas stream |
US6620401B1 (en) | 2001-07-13 | 2003-09-16 | Chevron U.S.A. Inc. | Zeolite SSZ-60 composition of matter and synthesis thereof |
US6461578B1 (en) * | 2001-07-13 | 2002-10-08 | Chevron U.S.A. Inc. | Using zeolite SSZ-59 for reduction of oxides of nitrogen in a gas stream |
US6461580B1 (en) * | 2001-07-13 | 2002-10-08 | Chevron U.S.A. Inc. | Using zeolite SSZ-58 for reduction of oxides of nitrogen in a gas stream |
WO2003045547A2 (en) * | 2001-11-26 | 2003-06-05 | Atofina Research | Composition based on a ferrierite and its use in a gas treatment method for reducing nitrogen oxide emissions |
WO2003045547A3 (en) * | 2001-11-26 | 2004-01-22 | Atofina Res | Composition based on a ferrierite and its use in a gas treatment method for reducing nitrogen oxide emissions |
EP1316359A1 (en) * | 2001-12-03 | 2003-06-04 | Rhodia Electronics and Catalysis | Process for the reduction of nitrogen oxide emissions using a ferrierite |
KR100453380B1 (en) * | 2001-12-27 | 2004-10-15 | 한국가스공사 | Cocation exchange ferrierite catalyst for and mothod of removing nitrogen oxide |
US20050100493A1 (en) * | 2003-11-06 | 2005-05-12 | George Yaluris | Ferrierite compositions for reducing NOx emissions during fluid catalytic cracking |
US9931595B2 (en) | 2003-11-06 | 2018-04-03 | W. R. Grace & Co.-Conn. | Ferrierite composition for reducing NOx emissions during fluid catalytic cracking |
US20050230285A1 (en) * | 2004-04-15 | 2005-10-20 | George Yaluris | Compositions and processes for reducing NOx emissions during fluid catalytic cracking |
US20050232839A1 (en) * | 2004-04-15 | 2005-10-20 | George Yaluris | Compositions and processes for reducing NOx emissions during fluid catalytic cracking |
US7304011B2 (en) | 2004-04-15 | 2007-12-04 | W.R. Grace & Co. -Conn. | Compositions and processes for reducing NOx emissions during fluid catalytic cracking |
US7641787B2 (en) | 2004-04-15 | 2010-01-05 | W.R. Grace & Co.-Conn. | Compositions and processes for reducing NOx emissions during fluid catalytic cracking |
US7918991B2 (en) | 2005-04-27 | 2011-04-05 | W. R. Grace & Co.-Conn. | Compositions and processes for reducing NOx emissions during fluid catalytic cracking |
US10656130B2 (en) * | 2016-05-17 | 2020-05-19 | Thermo Fisher Scientific (Bremen) Gmbh | Elemental analysis system and method with a reactor having two metal zeolite nitrogen oxides reduction reaction zones |
CN110026185A (en) * | 2018-11-23 | 2019-07-19 | 江苏中创清源科技有限公司 | A kind of modified perovskite type catalyst and preparation method thereof |
Also Published As
Publication number | Publication date |
---|---|
EP0434063B1 (en) | 1997-03-12 |
AU6828190A (en) | 1991-08-29 |
CA2032799C (en) | 1996-01-30 |
DE69030161T2 (en) | 1997-08-14 |
CA2032799A1 (en) | 1991-06-22 |
DE69030161D1 (en) | 1997-04-17 |
AU634005B2 (en) | 1993-02-11 |
EP0434063A1 (en) | 1991-06-26 |
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